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fundamentals of engineering supplied-reference handbook - Ventech!

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WASTEWATER TREATMENT AND<br />

TECHNOLOGIES<br />

Activated Sludge<br />

θcY<br />

( So<br />

− Se<br />

)<br />

X A =<br />

, where<br />

θ 1+<br />

k θ<br />

( )<br />

d<br />

c<br />

XA = biomass concentration in aeration tank (MLSS or<br />

MLVSS kg/m 3 );<br />

So = influent BOD or COD concentration (kg/m 3 );<br />

Se = effluent BOD or COD concentration (kg/m 3 );<br />

kd = microbial death ratio; kinetic constant; day −1 ;<br />

typical range 0.1–0.01, typical domestic wastewater<br />

value = 0.05 day –1 ;<br />

Y = yield coefficient Kg biomass/Kg BOD consumed;<br />

range 0.4–1.2; and<br />

θ = hydraulic residence time = Vol / Q<br />

VolX A<br />

θc = Solids residence time =<br />

QwXw + QeXe M ( 100)<br />

Vols = Sludge volume/day:<br />

Qs<br />

=<br />

ρs<br />

( % solids)<br />

Solids loading rate = Q X/A<br />

For activated sludge secondary clarifier Q = Qo + QR<br />

Organic loading rate (volumetric) = QoSo /Vol<br />

Organic loading rate (F:M) = QoSo /(Vol XA)<br />

Organic loading rate (surface area) = QoSo /AM<br />

Sludge volume after<br />

SVI =<br />

MLSS<br />

Type <strong>of</strong> Process<br />

settling(<br />

mL/L)<br />

( mg/L)<br />

* 1,000<br />

159<br />

ENVIRONMENTAL ENGINEERING (continued)<br />

Steady State Mass Balance around Secondary Clarifier:<br />

(Qo + QR)XA = Qe Xe + QR Xw + Qw Xw<br />

A = surface area <strong>of</strong> unit,<br />

AM = surface area <strong>of</strong> media in fixed-film reactor,<br />

Ax = cross-sectional area <strong>of</strong> channel,<br />

M = sludge production rate (dry weight basis),<br />

Qo = flow rate, influent<br />

Qe = effluent flow rate,<br />

Qw = waste sludge flow rate,<br />

ρs = wet sludge density,<br />

R = recycle ratio = QR/Qo<br />

QR = recycle flow rate = QoR,<br />

Xe = effluent suspended solids concentration,<br />

Xw = waste sludge suspended solids concentration,<br />

Vol = aeration basin volume,<br />

Q = flow rate.<br />

DESIGN AND OPERATIONAL PARAMETERS FOR ACTIVATED-SLUDGE<br />

TREATMENT OF MUNICIPAL WASTEWATER<br />

Mean cell<br />

Volumetric<br />

Food-to-mass ratio<br />

residence<br />

loading<br />

(kg BOD5/kg<br />

time<br />

(Vol-kg<br />

MLSS)<br />

(θc, d)<br />

BOD5/m 3 Hydraulic<br />

Mixed liquor<br />

residence<br />

suspended Recycle<br />

time in<br />

Flow<br />

solids ratio<br />

aeration<br />

regime*<br />

(MLSS, (Qr /Q)<br />

) basin<br />

mg/L)<br />

(θ, h)<br />

BOD5<br />

removal<br />

efficiency<br />

(%)<br />

Air <strong>supplied</strong><br />

(m 3 /kg<br />

BOD5)<br />

Tapered aeration 5−15 0.2−0.4 0.3−0.6 4−8 1,500−3,000 0.25−0.5 PF 85−95 45−90<br />

Conventional 4−15 0.2−0.4 0.3−0.6 4−8 1,500−3,000 0.25−0.5 PF 85−95 45−90<br />

Step aeration 4−15 0.2−0.4 0.6−1.0 3−5 2,000−3,500 0.25−0.75 PF 85−95 45−90<br />

Completely mixed 4−15 0.2−0.4 0.8−2.0 3−5 3,000−6,000 0.25−1.0 CM 85−95 45−90<br />

Contact stabilization 4−15 0.2−0.6 1.0−1.2 0.25−1.0 45−90<br />

Contact basin 0.5−1.0 1,000−3,000 PF 80−90<br />

Stabilization basin 4−6 4,000−10,000 PF<br />

High-rate aeration 4−15 0.4−1.5 1.6−16 0.5−2.0 4,000−10,000 1.0−5.0 CM 75−90 25−45<br />

Pure oxygen 8−20 0.2−1.0 1.6−4 1−3 6,000−8,000 0.25−0.5 CM 85−95<br />

Extended aeration 20−30 0.05−0.15 0.16−0.40 18−24 3,000−6,000 0.75−1.50 CM 75−90 90−125<br />

♦ Metcalf and Eddy, Wastewater Engineering: Treatment, Disposal, and Reuse, 3rd ed., McGraw-Hill, 1991 and McGhee, Terence and E.W. Steel, Water Supply and Sewerage, McGraw-Hill, 1991.<br />

*PF = plug flow, CM = completely mixed.

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